Abstract
Twenty-three extremely acidic (pH between 2.5 and 3.5) mining lakes in Lusatia (Germany) were analysed in order to classify their hydrochemistries and to assist the understanding of phytoplankton colonization of these extreme environments. Neither morphometric nor physical parameters influence phytoplankton composition but determine the extent to which the nutrient supply supports the mass development of Chrysophyceae and Chlorophyceae in certain layers of the water (hypo- or epilimnetic chlorophyll maxima and short mass developments). Conventional trophic classification is not readily applicable to these lakes but a chemical classification on the basis of hydrogen, total iron and acidity is proposed. Species of Ochromonas and Chlamydomonas dominate the phytoplankton in fourteen of the most acid lakes; dinoflagellates occurre additionally in four; a more diverse algal assemblage with diatoms and cryptophytes is found in lakes with moderately acidic (pH 5.7–7.0) or alkaline conditions (pH 7.0–9.4). The lake chemistry is the main determinant for the planktonic composition of the water bodies whereas the trophic state mainly determines the level of algal biomass.
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Albertano, P., G. Pinto, S. Santisi & R. Taddei, 1981. Spermatozopsis acidophila Kalina (Chlorophyta, Volvocales), a little known algae from highly acidic environments. Giorn. Bot. Ital. 115: 65–76.
Albertano, P., G. Pinto & A. Pollio, 1994. Ecophysiology and ultrastructure of an acidophilic species of Ochromonas (Chrysophyceae, Ochromonadales). Arch. Protistenk. 144: 75–82.
Almer, B., W. Dickson, C. Ekström, E. Hörnström & U. Miller, 1974. Effects of acidification on Swedish lakes. Ambio 3: 30–36.
Andersson, A., S. Falk, G. Samuelsson & A. Hagström, 1989. Nutritional characteristics of a mixotrophic nanoflagellate, Ochromonas sp. Microb. Ecol. 17: 251–262.
Arvola, L., K. Salonen, P. Kankaala & A. Lehtovaara, 1992. Vertical distributions of bacteria and algae in a steeply stratified humic lake under high grazing pressure from Daphnia longispina. Hydrobiologia 229: 253–269.
Benndorf, J., 1994. Sanierungsmaβnahmen in Binnengewä ssern: Auswirkungen auf die trophische Struktur. Limnologica 24: 121– 135.
Blouin, A. C., 1989. Patterns of plankton species, pH and associated water chemistry in Nova Scotia lakes. Wat. Air Soil Pollut. 46: 343–358.
Boavida, M. J. & R. T. Heath, 1986. Phosphatase activity of Chlamydomonas acidophila Negoro (Volvocales, Chlorophyceae). Phycologia 25: 400–404.
DEV, 1986–1993. Deutsche Einheitsverfahren zur Wasser, Abwasserund Schlammuntersuchung. Verlag Chemie, Weinheim.
Eriksson, M. O. G., L. Henrikson, B. I. Nilsson, G. Nyman, H. G. Oscarson & A. E. Stenson, 1980. Predatorprey relations, important for biotic changes in acidified lakes. Ambio 9: 248– 249.
Geller, W., H. Klapper & M. Schultze, 1998. Natural and anthropogenic sulfuric acidification of lakes. In W. Geller, H. Klapper & W. Salomons (eds), Acidic mining lakes. Springer Verlag: 3–14.
Goldman, J. C., W. J. Oswald & D. Jenkins, 1974. The kinetics of inorganic carbon limited algal growth. J. WPCF 46: 554–574.
Gromov, B., V. N. Nikitina, & K.A. Mamkayeva, 1991. Ochromonas vulcania sp. nov. (Chrysophyceae) from the acidic spring on the Kunashir Island (Kurile Islands). Algologia 1: 76–79.
Jannson, M., 1981. Induction of high phosphatase activity by aluminium in acid lakes. Arch. Hydrobiol. 93: 32–44.
Jones, R. I., 1994. Mixotrophy in planctonic protists as a spectrum of nutritional strategies. Mar. Microb. Food Webs 8: 87–96.
Klapper, H. & M. Schultze, 1995. Geogenically acidified mining lakes – living conditions and possibilities of restoration. Int. Revue ges. Hydrobiol. 80: 639–653.
Klapper, H., K. Friese, B. Scharf, M. Schimmele & M. Schultze, 1998. Ways of controlling acid by ecotechnology. In W. Geller, H. Klapper & W. Salomons (eds), Acidic mining lakes. Springer Verlag: 401–416.
Kwiatkowski, R. E. & J. C. Roff, 1976. Effects of acidity on the phytoplankton and primary productivity of selected northern Ontario lakes. Can. J. Bot. 54: 2546–2561.
Lackey, J. B., 1939. Aquatic life in waters polluted by acid mine waste. Meet. Limnol. Soc. Am. 5: 740–746.
Laliberté, G. & J. de la Noüe, 1993. Auto, hetero-and mixotrophic growth of Chlamydomonas humicola (Chlorophyceae) on acetate. J. Phycol. 29: 612–620.
Mischke, U., J. Rücker, M. Kapfer & B. Nixdorf, 1994. Besiedlungsstruktur und Interaktionen im Plankton geogen versauerter Tagebaurestseen der Lausitz. Deutsche Gesellschaft f ür Limnologie: Erweiterte Zusammenfassungen der Jahrestagung 1994 in Hamburg: 700–704.
Nixdorf, B., J. Rücker, R. Deneke & P. Zippel, 1995a. Limnologische Zustandsanalyse von Standgewä ssern im Scharmützelseegebiet – Teil 1. BTU CottbusUW aktuelle Reihe 1/95.
Nixdorf, B., J. Rücker, B. Köcher & R. Deneke, 1995b. Erste Ergebnisse zur Limnologie von Tagebaurestseen in Brandenburg unter besonderer Berücksichtigung der Besiedlung im Pelagial. Limnologie Aktuell No.7: 39–52.
Nixdorf, B. K., K. Wollmann & R. Deneke, 1998: Ecological potentials for planktonic development and food web interactions in extremely acidic mining lakes in Lusatia (Eastern Germany). In W. Geller, H. Klapper & W. Salomons (eds), Acidic mining lakes. Springer Verlag: 147–168.
OECD, 1982. Eutrophication of waters – Monitoring, assessment and control. OECD, Paris.
Pinto, G. & R. Taddei, 1978. Le alghe delle acque e dei suoli acidi italiani. Delpinoa 18–19: 77–106.
Porter, K. G. & Y. S. Feig, 1980. The use of DAPI for identifying and counting aquatic microflora. Limnol. Oceanogr. 25: 943–948.
Rhodes, R. G., 1981. Heterothallism in Chlamydomonas acidophila Negoro isolated from acidic stripmine ponds. Phycologia 20: 81–82.
Satake, K. & Y. Saijo, 1974. Carbon dioxide content and metabolic activity of microorganisms in some acid lakes in Japan. Limnol. Oceanogr. 19: 331–338.
Satake, K. & Y. Saijo, 1978. Mechanism of lamination in bottom sediment of the strongly acid Lake Katanuma. Arch. Hydrobiol. 83: 429–442.
Schindler, D. W. & S. K. Holmgren, 1971. Primary production and phytoplankton in the Experimental Lakes Area, northwestern Ontario, and other low carbonate waters, and a liquid scintillation method for determining C14 activity in photosynthesis. J. Fish. Res. Bd. Can. 28: 189–201.
Schultze, M., H. Klapper, B. Nixdorf, U. Mischke & U. Grünewald, 1994. Methodik zur limnologischen Untersuchung und Bewertung von Bergbaurestseen. Bund-L änder Arbeitsgruppe Wasserwirtschaftliche Planung.
Sheath, R. G., M. Havas, J. A. Hellebust & T. C. Hutchinson, 1982. Effects of long-term natural acidification on the algal communities of tundra ponds at the Smoking Hills, N.W.T., Canada. Can. J. Bot. 60: 58–72.
Steinberg, C., H. Schäfer & W. Beisler, 1998. Do acid-tolerant cyanobacteria exist? Acta hydrochim. hydrobiol. 26: 13–19.
TGL 27885/01, 1982. Fachbereichstandard-Nutzung und Schutz der GewässerStehende Binnengewässer, Klassifizierung, DDR.
Twiss, M. R., 1990. Copper tolerance of Chlamydomonas acidophila (Chlorophyceae) isolated from acidic, copper-contaminated soils. J. Phycol. 26: 655–659.
Utermöhl, H., 1958. Zur Vervollkommnung der quantitativen Phytoplanktonmethodik. Mitt. int. Ver. Limnol. 9: 1–38.
Whitton, B. A. & B. M. Diaz, 1981. Influence of environmental factors on photosynthetic species composition in highly acidic waters. Verh. int. Ver. Limnol. 21: 1459–1465.
Yan, N. D., 1979. Phytoplankton community of an acidified, heavy metal-contaminated lake near Sudbury, Ontario: 1973–1977. Wat. Air Soil Pollut. 11: 43–55.
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Nixdorf, B., Mischke, U. & Leßmann, D. Chrysophytes and chlamydomonads: pioneer colonists in extremely acidic mining lakes (pH <3) in Lusatia (Germany). Hydrobiologia 369, 315–327 (1998). https://doi.org/10.1023/A:1017010229136
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DOI: https://doi.org/10.1023/A:1017010229136